Detection of phenols using engineered bacteria

ABSTRACT

Detection of phenols using engineered bacteria. A biosensor can be created by placing a reporter gene under control of an inducible promoter. The reporter gene produces a signal when a cognate transcriptional activator senses the inducing chemical. Creation of bacterial biosensors is currently restricted by limited knowledge of the genetic systems of bacteria that catabolize xenobiotics. By using mutagenic PCR to change the chemical specificity of the  Pseudomonas  species CF600 DmpR protein, the potential for engineering novel biosensors for detection of phenols has been demonstrated. DmpR, a well-characterized transcriptional activator of the P. CF600&#39;s dmp operon mediates growth on simple phenols. Transcription from Po, the promoter heading the dmp operon, is activated when the sensor domain of DmpR interacts with phenol and mono-substituted phenols. By altering the sensor domain of the DmpR, a group of DmpR derivatives that activate transcription of a Po-lacZ fusion in response to eight of the EPA&#39;s eleven priority pollutant phenols has been created. The assays and the sensor domain mutations that alter the chemical specificity of DmpR is described.

CROSS-REFERENCE TO RELATED APPLICATIONS

This application is a Divisional of U.S. patent application Ser. No. 09/520,538, filed Mar. 8, 2000, now U.S. Pat. No. 6.773,918, which claims the benefit of United States provisional patent application No. 60/123,659 filed Mar. 9, 1999.

This invention was made with government support under Contract No. W-7405-ENG-36 awarded by the U.S. Department of Energy to The Regents of The University of California. The government has certain rights in the invention.

FIELD OF THE INVENTION

The present invention relates generally to the detection of organic pollutants and, more particularly, to the mutagenic generation of a group of DmpR protein derivatives with improved ability to activate transcription of a reporter gene in bacteria in the presence of phenols, including certain disubstituted phenols, in liquids and soils.

BACKGROUND OF THE INVENTION

In the last three decades, there has been a significant increase in government regulations that hold industrial entities accountable for the chemical pollution that results from their manufacturing activities. In order to comply with environmentally sensitive regulations, businesses must be able to identify contamination and monitor its remediation processes. The cost and technical complexity of chromatographic methods currently in use may act to limit characterization of contaminated sites. One way to lower the cost of detection is to use biosensors derived from genetic systems of bacteria that have evolved to use organic contaminants as growth substrates.

Certain strains of soil bacteria have evolved the capacity to use toxic organic chemicals as food sources. Production of the required metabolic enzymes is, in some cases, controlled by a particular type of regulatory protein that detects the toxic chemical through a direct physical interaction. The protein-chemical complex binds to a cognate promoter sequence and activates expression of genes encoding the required metabolic enzymes. This type of regulatory protein can be utilized as a pollution detecting component in bacteria that have been engineered to signal the presence of environmental pollution.

The most basic whole cell bacterial biosensors are created by placing a reporter gene under control of an inducible promoter. Expression of the reporter gene provides a measurable signal when the appropriate transcription activator protein interacts with an effector chemical.

Phenol and various substituted phenols are used in the manufacture of dyes, photographic chemicals, pesticides, lumber preservatives, microbiocides and herbicides. Current methods for detecting phenol contaminants include gas chromatography and high-pressure liquid chromatography. These chromatographic methods require expensive equipment and highly trained technicians. In response to the U.S. Environmental Protection Agency having listed eleven phenols as priority pollutants, industries that use phenol and phenol derivatives require simple and inexpensive detection methods to identify spills, leaks, and other phenol contamination that result from their manufacturing and service activities.

The construction of bacterial biosensors is limited by the restricted availability of bacteria that are known to metabolize a chemical of interest and, in particular, by the absence of knowledge concerning the genetic systems that control bacterial response to the chemical. Fortunately, some of the bacterial genetic systems that support metabolism of polluting chemicals show significant genetic relatedness. Operons encoding genes required for metabolism of phenol, toluene, benzene, and xylene in some Pseudomonas and Acinetobacter species are headed by promoters recognized by sigma-54-associated RNA polymerase. Transcription directed by these promoters occurs when the system's regulatory protein detects the presence of the substrate for the catabolic enzymes. Proteins in this category include DmpR, XylR, MopR, PhhR, PhlR, and TbuT. These six proteins show significant similarity to one another at the amino acid level. Sequence information and domain swapping experiments indicate that the general arrangement of these regulatory proteins consists of discrete areas with three independent functions including chemical detection, polymerase activation, and DNA-binding.

XylR and DmpR are the most studied members of this group of transcription activators. The Pseudomas putida XylR has already served as the detection component for a number of biosensors based on its ability to activate transcription in response to xylene, toluene and benzene. DmpR, the product of the Pseudomonas CF600 dmpR gene, mediates expression of the dmp operon to allow growth on simple phenols. Transcription from Pdmp, the promoter heading the dmp operon, is activated when DmpR senses the presence of phenol, cresols, mono-chlorinated phenols, and some mono-methylated phenols (See, e.g., V. Shingler and T. Moore, “Sensing of aromatic compounds by the DmpR transcriptional activator of phenol-catabolizing Pseudomonas sp. strain CF600”, J. Bacteriol. 176:1555-1560 (1994)). Disubstituted phenols, such as 2,4-dichlorophenol or 2,4-dimethylphenol, are inferior inducers of dmp transcription.

Domain swapping experiments to form XylR-DmpR hybrids demonstrated that the sensor activity of these regulatory proteins is localized to the amino terminal region.

By switching the first 234 amino acids of DmpR with those from XylR, Shingler and Moore, supra, created a chimeric protein that activated transcription from Pdmp in response to toluene and xylene, but not phenol or cresol. The results of the hybrid protein experiments indicated that transcription from Pdmp depends on a direct physical interaction between the sensor domain of DmpR and the inducing phenol.

The single regulatory protein, and the independent domain arrangement of DmpR and other proteins of this type make them particularly suitable candidates for genetic manipulation and suggests a way around the restrictions imposed by limited information about the genetics that control bacterial degradation of xenobiotics. Such altered proteins have the potential to extend the chemical target range of biosensors beyond that based on natural systems.

Therefore, it is an object of the present invention to alter the chemical sensing domain of the protein DmpR to respond to phenol and phenol derivatives which are poorly detected or undetected by the wild type protein.

Another object of the invention is to alter the chemical sensing domain of the protein DmpR to respond to phenol and phenol derivatives without disturbing its transcription activating functions.

Additional objects, advantages and novel features of the invention will be set forth in part in the description which follows, and in part will become apparent to those skilled in the art upon examination of the following or may be learned by practice of the invention. The objects and advantages of the invention may be realized and attained by means of the instrumentalities and combinations particularly pointed out in the appended claims.

SUMMARY OF THE INVENTION

To achieve the foregoing and other objects, and in accordance with the purposes of the present invention, as embodied and broadly described herein, the method for enhancing bacterial response to organic molecules, where the bacteria have a regulatory protein with discrete functional domains for independent activities, one such domain being a sensor domain that detects the organic molecules through a direct physical interaction forming a protein-molecule complex which binds to a cognate promoter sequence and activates expression of genes encoding metabolic enzymes, includes modifying the sensor domain of the regulatory protein such that the response to the organic molecule is enhanced without altering the other domains.

Benefits and advantages of the present invention include the creation of a large variety of engineered proteins with abilities to detect toxic organic chemicals. Such engineered proteins will be useful in development of environmentally beneficial tools that both detect and degrade polluting chemicals.

BRIEF DESCRIPTION OF THE DRAWINGS

The accompanying drawings, which are incorporated in and form a part of the specification, illustrate an embodiment of the present invention and, together with the description, serve to explain the principles of the invention. In the drawings:

FIG. 1 shows the organization of the DmpR protein and illustrates the domains having distinct functions which made it possible to modify the protein's sensor domain to change its capacity for interacting with a particular phenol without destroying its ability to bind DNA and activate transcription form its cognate promoter Pdmp.

FIG. 2 a shows the results of a β-galactosidase assay for the detection of 2-chlorophenol, while FIG. 2 b shows the assay for 2,4-dichlorophenol using the bacterial test strain containing either wild type DmpR or the derivative DmpR-B21, where NI indicates a negative control containing no inducer (no phenol).

FIG. 3 a shows assays comparing wild type DmpR and DmpR-B23 as detectors for six concentrations of 2-chlorophenol after a 60 minute exposure, while FIG. 3 b shows assays comparing the response of wild type DmpR and DmpR-B17#2 to six concentrations of 4-chloro-3-methylphenol.

FIG. 4 a shows that a four-hour exposure to phenols increases the detection signal (in β-galactosidase activity units) for low concentrations of 2-chlorophenol for DmpR-B23, whereas FIG. 4 b shows the response of DmpR-B17#2 to low concentrations of 2,4-dichlorophenol, 2-nitrophenol, and 4-nitrophenol.

FIG. 5 a compares the detection of 2,4-dichlorophenol by DmpR-B9 with that of the wild type DmpR for unsubstituted phenol shown in FIG. 5 b in contaminated soil, unsubstituted phenol being a natural effector of wild type DmpR.

FIG. 6 a compares the detection of 2-chlorophenol, 2,4-dimethylphenol, and 4-nitrophenol by wild type DmpR with that for the engineered protein DmpR-B31, while FIG. 6 b compares the detection of 2,4-dichlorophenol and 4-chloro-3-methylphenol by the wild type DmpR and DmpR-D12; DmpR-B31 showing a strong response to most substituted phenols, but having a relatively high uninduced (NI) value.

FIG. 7 a compares the detection of 2-chlorophenol by DmpR-D9 with its detection by wild type DmpR, while FIG. 7 b compares the detection of 2-nitrophenol by DmpR-D9 with that for wild type DmpR.

DETAILED DESCRIPTION

Briefly, the present invention includes a method for creating mutant DmpR derivatives having increased response to phenol and substituted phenols. These mutant derivatives are shown to activate the transcription of a reporter gene in the presence of the seven phenols listed as priority pollutants by the U.S. Environmental Protection Agency. Codon changes, including three silent mutations, that improve DmpR's ability to detect disubstituted phenols including 2,4-dichlorophenol and 2,4-dimethylphenol are described for both liquid and soil assays. Additionally, the mutations improve the ability of DmpR to detect di-substituted 4-chloro-3-methyl phenol and mono-substituted 2-chlorophenol, 2-nitrophenol, and 4-nitrophenol. Regulatory proteins capable of detecting organic contaminants through a specific physical interaction have been identified in some Pseudomonas and Acinetobacter species. Proteins of this type include DmpR, XylR, MopR, PhhR, PhlR, and TbuT. The general arrangement of these proteins consists of discrete functional domains with independent activities. The highly conserved carboxyl and middle regions of these proteins contain regions dedicated to DNA-binding and transcription activation. The less-conserved amino terminal region is known as the sensor domain and is the portion of the protein that physically interacts with (detects) a specific chemical. For example, DmpR, MopR, PhhR, and PhlR detect phenol and activate production of enzymes that metabolize phenol. Chemicals detected by XylR and TbuT include toluene and xylene.

Because of their distinct functional domain organization, proteins of this kind are particularly suitable to genetic modification. A key element in the present invention is the mutagenic modification of DNA corresponding to a protein's sensor domain because this region can be mutagenized without changing the protein's ability to bind DNA and activate gene expression from its cognate promoter. Modification of a sensor domain has potential for creating novel proteins with altered or improved chemical detection ability.

Mutations in the sensor domain of DmpR were generated through mutagenic PCR. Engineered genes were transformed into bacterial test strains that carried DmpR's cognate promoter fused to a reporter gene. This test strain allowed identification and characterization of novel versions of DmpR with chemical detection capabilities that significantly differ from that of the wild type protein. Engineered derivatives of DmpR detect 2,4-dichlorophenol and 2,4-dimethylphenol, as well as other phenolic molecules that are not detected by wild type DmpR.

Reference will now be made in detail to the present preferred embodiments of the present invention, examples of which are shown in the accompanying drawings. Turning now to FIG. 1, the dmpR wt-N gene (See, e.g., Shingler and Moore, supra) carried on plasmid pAW50 served as the template for amplification of the dpmR sensor domain by mutagenic polymerase chain reaction (PCR). The products resulting from the mutagenic PCR were digested using NdeI and SacII and ligated back into a pAW50 plasmid fragment, from which the wild type NdeI-SacII region had been removed. This procedure resulted in replacement of DNA corresponding to the first 175 amino acids of DmpR (about 85% of the sensor domain). Ligation products were electroporated into AW101 (trp::Pdmp-lacZ fusion). Transformants were initially selected for tetracycline resistance and then replicated onto plates containing X-gal and one of the test phenols. Colonies that developed more blue color than colonies containing wild type DmpR were selected for further analysis with liquid β-galactosidase assays. β-galactosidase activity is proportional to transcription of the Pdmp-lacZ reporter fusion and is, therefore, a measure of particular variant DmpR's ability to detect phenol or specific substituted phenols. This mutagenic procedure led to the identification of more than twenty DmpR derivatives with altered response to phenols. Five of these derivatives are representative of proteins which show significant promise as effective detectors of phenols listed as primary pollutants by the U.S. Environment Protection Agency.

Having generally described the invention, the following EXAMPLE provides additional details.

EXAMPLE

A. Bacterial strains and plasmids. E. coli TE2680 (Elliot, T. 1992. “A method for constructing single-copy lac fusions in Salmonella typhimurium and its application to the hemA-prfA operon,” J. Bacteriol. 174:245-253) was used as an intermediate strain for placing the Pdmp-lacZ fusion into the chromosome of E. coli MC4100 (Casadaban, M. 1976. “Transposition and fusion of the lac genes to selected promoters in Escherichia coli using bacteriophage, lambda and Mu,” J. Mol. Biol. 104:541-555) to create the dmpR test strain AW101. DH5a (Sambrook, J. E. F. Fritsch, and T. Maniatis. 1989. Molecular Cloning: A Laboratory Manual, 2nd Edition. Cold Springs Harbor Laboratory Press. Plainview, N.Y.) was host for plasmid constructions.

pVI401 (See, e.g., Shingler and Moore, supra) served as the source of both the dmpR wt-N gene and the Pdmp promoter which heads the divergently transcribed dmp operon. dmpR wt-N contains a synthetic NdeI restriction site resulting from nucleotide changes immediately upstream from the ATG initiation codon. The coding region of dmpR wt-N remains the same as that of wild type dmpR and the response of the encoded protein to aromatic chemicals is indistinguishable from that produced from the wild type dmpR gene (Shingler et al, supra).

pRS551 (Simons, R. W., F. Houman, and N. Kleckner. 1987. “Improved single and multicopy lac-based cloning vectors for protein and operon fusions,” Gene 53:85-96.), a promoter assay vector, contains homology to the engineered trp operon of strain TE2680 and thus, allows integration of promoter-lacZ fusions into the E. coli chromosome. pAW51 is a derivative of pRS551 that carries the dmp operon promoter Pdmp on a 0.6 kb DNA fragment fused to the pRS551 lacZ reporter gene.

pAW50 was derived from pBR322 (New England Biolabs, Beverly, Mass.). Following removal of the pBR322 NdeI site, a 2.4 kb NotI fragment containing dmpR wt-N was cloned into a NotI linker which replaced the ScaI site normally located in the ampicillin resistance gene of pBR322. An EcoRI restriction digest followed by ligation removed the promoter of the ampicillin resistance gene, as well as the 5′ Not I site. pAW50 contains dmpR sequences extending approximately 650 base pairs upstream from the dmpR translation initiation site.

B. Genetic techniques. Plasmid DNA was isolated using a Qiagen Plasmid Kit (Qiagen, Inc., Chatsworth, Calif.) or by a mini-prep alkaline lysis method (Lee, S-y, and S. Rasheed. 1990. “A simple procedure for maximum yield of high-quality plasmid DNA,” Biotechniques 9:676-679). Standard methods were used for restriction digests, gel electrophoresis and ligations. Transformation of E. coli was done by the electroporation method (Dower, W. J., J. F. Miller, and C. W. Ragsdale. 1988. “High efficiency transformation of E. coli by high voltage electroporation,” Nucleic Acids Res. 16:6127-6145) using a Bio-Rad Gene Pulser II unit (Bio-Rad, Hercules, Calif.). Standard PCR to amplify the Po fragment was done as described by Innes et al. (Innes, M. A., D. H. Gelfand, J. J. Sninsky, and T. J. White. 1990. PCR Protocols: a Guide to Methods and Applications, Academic Press, New York.).

pVI401 (See, e.g., Shingler and Moore, supra) served as the template for amplifying Po in a reaction that included primers Pdmp5′-EcoRI (5′-CCATCGCTGAATTCTGCAGCMCAG-3′), SEQ ID No. 8 hereof, and Pdmp3′-BamHI (5′-CGCACACGGATCCMCGAGTGAG-3′), SEQ ID No. 9 hereof. Primers were synthesized on an Applied Biosystems DNA/RNA Synthesizer 394 (Applied Biosystems, Inc. Foster City, Calif.) in the DNA synthesis laboratory of the Life Sciences Division at LANL. PCR was carried out on a Perkin-Elmer 9600 thermal cycler with a 2 minute denaturation step at 92° C. followed by 25 cycles of one minute each at the following temperatures: 92° C., 52° C., and 72° C. The Po PCR product was digested with BamHI and EcoRI to allow directed cloning in front of the promoterless lacZ gene of pRS551 for creation of the Pdmp-lacZ fusion of pAW51.

Mutagenic PCR to change the DmpR sensor domain was done by a modification of Cadwell and Joyce's method (Cadwell, R. C., and G. F. Joyce. 1995. Mutagenic PCR, p. 583-589. In C. W. Dieffenbach and G. S. Dveksler (ed.), PCR Primer, A Laboratory Manual. Cold Spring Harbor Laboratory Press. Cold Spring Harbor, N.Y.). pAW50 served as template in the mutagenic PCR reaction with 25 pmoles each of the following primers: dmpR5′-75 (5′-GCCGTCGATTGATCATTTGG-3′), SEQ ID No. 10 hereof, and dmpR3′-976, (5′-TGTCCATCATATTGCGCACG-3′), SEQ ID No. 11 hereof. In addition, the reaction contained 5 mM MgCl₂, 0.5 mM MnCl₂, 0.2 mM dATP and dGTP, 0.8 mM dCTP and dTTP, 10 mM Tris-HCl (pH 8.3), 50 mM KCl, 0.001% (wt/vol) gelatin, and 5 units of AmpliTaq polymerase (Perkin Elmer, Foster City, Calif.). The mutagenic PCR amplification cycle followed a 2 min. denaturation at 92° C. and consisted of 30 cycles of 94° C. (10 s), 56° C. (20 s) and 72° C. (1 min.).

pAW50 and the mutagenized PCR products were each digested with NdeI and SacII. The 525 base pair NdeI-SacII PCR fragment contained most of the dmpR sensor domain. This fragment and pAW50, excluding the wild type sensor domain, were gel purified from low melting point agarose using Elutip-D columns (Schleicher and Schell, Keene, N.H.). The purified DNA fragments served as components in a ligation reaction to reassemble pAW50 derivatives carrying dmpR with variously mutated sensor regions.

C. Test strain construction and screen for sensor domain mutations. pAW51, carrying the Pdmp-lacZ fusion, was linearized through restriction with ScaI, which cuts at a single site within the vector ampicillin resistance gene. The linearized plasmid was then used to transform TE2680 to kanamycin resistance. Transformants were screened for loss of ampicillin and chloramphenicol resistance, a condition indicating integration of the Pdmp-lacZ fusion into the TE2680 chromosome at the trp operon. The general transducing phage P1 kc (American Type Culture Collection, Rockville, Calif.) was used to transfer the fusion to the chromosome of MC4100 resulting in strain AW101.

AW101 was used as a test strain to identify and characterize changes in DmpR's sensing capacity subsequent to sensor domain mutagenesis. pAW50 derivatives were electroporated into AW101 and transformants were selected on Luria-Bertani (Difco, Detroit, Mich.) plates containing 10.5 μg/ml tetracycline. Transformants were then replicaplated onto M9 minimal medium (10) plates containing 0.2% glucose, 30 μg/ml tryptophan, 1 μg/ml thiamine, 10.5 μg/ml tetracycline, 0.25% 5-bromo-4-chloro-3-indoyl-β-D-galactoside (X-Gal), and either no inducer (NI) or 0.05 mM of a phenol derivative. Cells that formed blue colonies on plates containing a phenol derivative were subject to liquid β-galactosidase assays.

D. β-Galactosidase Assays. Overnight cultures of AW101 carrying pAW50 derivatives were diluted 1000-fold into Luria-Bertani broth containing 10.5 μg/ml tetracycline. When cells reached an OD₅₉₅ nm between 0.60 and 0.90 as measured on a Lambda Bio uv/vis spectrophotometer (Perkin Elmer Corp. Analytical Instruments, Norwalk, Conn.), 500 μL samples were pelleted and immediately resuspended in 500 μL spent Luria-Bertani broth containing the appropriate phenol compound. Cell incubation was then continued with shaking at 37° C. for 2 h. Samples were pelleted and frozen at −70° C. for assay the following day.

Liquid β-galactosidase assays were performed using a modification of Miller's assay (Miller, J. H., 1972. “Experiments in Molecular Genetics,” Cold Spring Harbor Laboratory, Cold Spring Harbor, N.Y.). Cell sample pellets were thawed and resuspended in Z buffer. The optical density at 595 nm of each cell suspension was read in a microtiter plate using an automated microplate reader (BIO-TEK Instruments, Inc., Winooski, Vt.). Following the addition of 15 μL 0.1% sodium dodecyl sulfate and 25 μL HCCl₃, the remaining cell suspension was vortexed for 30 s to lyse cells. The reaction was begun with the addition of 50 μL o-nitrophenyl-β-D-galactopyranoside (2.5 mg/ml) to the lysed cells. Reactions were incubated at 26° C. until stopped with the addition of 50 μL 1M Na₂CO₃. Color development of the reactions was read at OD₄₁₅ on the microplate reader. Arbitrary units for graphing purposes were calculated as (1000×OD₄₁₅)/(time)(OD₅₉₅) where time is the reaction time in minutes. Equivalent cell volumes were read for both optical densities.

E. DNA Sequencing. Mutations in the dmpR sensor domains carried by pAW50 derivatives were identified using an ABI PRISM Dye Terminator Cycle Sequencing kit and following the manufacturer's (Perkin-Elmer) protocol. Electrophoresis of sequencing reactions was carried out on 4% polyacrylamide gels using an ABI 373A Stretch DNA Sequencer (Applied Biosystems, Inc., Foster City, Calif.). Analysis of mutant sensor domain DNA and amino acid sequences was done using DNASTAR LASERGENE software (DNASTAR Inc., Madison, Wis.).

FIG. 2 a shows the results of a β-galactosidase assay for the detection of 2-chlorophenol, while FIG. 2 b shows the assay for 2,4-dichlorophenol using the bacterial test strain containing either wild type DmpR or the derivative DmpR-B21 (SEQ ID No. 3), where NI indicates a negative control containing no inducer (no phenol). For all included graphs, units are β-galactosidase activity normalized for time length of assay and number of cells in assay. NI indicates a negative control containing no inducer (no phenol). Wild type DmpR has no apparent response to a 0.0025 mM solution of 2-chlorophenol (0.3 parts per million), whereas DmpR-B21 responds well with a 60-fold increase in β-galactosidase activity. 2-chlorophenol is a natural inducer of the wild type DmpR protein, as shown by its signal production (97 units) when exposed to a 0.025 mM solution of 2-chlorophenol. A more complex phenol, 2,4-dichlorophenol, elicits a response from DmpR-B21 at 0.025 mM (4 parts per million), but not from the natural DmpR protein. Note changes in axis between graphs.

FIG. 3 a shows assays comparing wild type DmpR and DmpR-B23 (SEQ ID No. 4 hereof) as detectors for six concentrations of 2-chlorophenol after a 60 minute exposure, while FIG. 3 b shows assays comparing the response of wild type DmpR and DmpR-B17#2 (SEQ ID No. 2 hereof) to six concentrations of 4-chloro-3-methylphenol. Both DmpR-B23 and DmpR-B17#2 are significantly better detectors of substituted phenols than the wild type protein at all concentrations assayed.

FIG. 4 a shows that a four-hour exposure to phenols increases the detection signal (in β-galactosidase activity units) for low concentrations of 2-chlorophenol for DmpR-B23, whereas FIG. 4 b shows the response of DmpR-B17#2 (SEQ ID No. 2 hereof) to low concentrations of 2,4-dichlorophenol, 2-nitrophenol, and 4-nitrophenol. DmpR-B23's response to 0.5 ppm 2-chlorophenol was more than 20-fold higher than that of the wild type DmpR protein. DmpR-B17#2 responds to low concentrations of phenols (2,4-dichlorophenol, 2-nitrophenol, and 4-nitrophenol) that are poor effectors of the wild type DmpR protein.

FIG. 5 a compares the detection of 2,4-dichlorophenol by DmpR-B9 (SEQ ID No. 1 hereof) with that for unsubstituted phenol shown in FIG. 5 b in contaminated soil, unsubstituted phenol being a natural effector of wild type DmpR. Detection of chemicals in contaminated soil is often difficult because soil may bind the phenols, making them less available to the test bacteria. However, DmpR-B9's capacity to detect phenols in soil remains significantly better than that of the wild type protein. The response of DmpR-B9 to 4 parts per million (ppm) 2,4-dichlorophenol in soil is six-fold higher than that of wild type DmpR. DmpR-B9's response to 2.5 ppm phenol is four-fold better than that of wild type.

FIG. 6 a compares the detection of 2,4-dichlorophenol, 2,4-dimethylphenol, and 4-nitrophenol by wild type DmpR with that for the engineered protein DmpR-B31 (SEQ ID No. 5 hereof), while FIG. 6 b compares the detection of 2,4-dichlorophenol and 4-chloro-3-methylphenol by the wild type DmpR and DmpR-D12 (SEQ ID No. 7 hereof). DmpR-B31 shows a strong response to most substituted phenols, but also has a relatively high uninduced (NI) value. DmpR-D12's detection of 10 ppm 4-chloro-3-methylphenol and 3 ppm 2,4-dichlorophenol are eight and 10-fold higher than that of wild type DmpR.

FIG. 7 a compares the detection of 2-chlorophenol by DmpR-D9 (SEQ ID No. 6) with its detection by wild type DmpR, while FIG. 7 b compares the detection of 2-nitrophenol by DmpR-D9 with that for wild type DmpR. DmpR-D9's response to 2-chlorophenol is nineteen-fold higher than that of the wild type protein, while its response to 2-nitrophenol is five times higher than that of wild type DmpR.

The foregoing description of the invention has been presented for purposes of illustration and description and is not intended to be exhaustive or to limit the invention to the precise form disclosed, and obviously many modifications and variations are possible in light of the above teaching. For example, it would be apparent to one having ordinary skill in the art after reading the present disclosure that mutating the sensor domain to enhance the response of bacteria to selected organic molecules could be achieved by removing the sensor domain from the bacterial DNA encoding the regulatory protein, subjecting the removed sensor domain to gene reshuffling, ligating the mutated sensor domain into the DNA encoding the regulatory protein, and testing the bacteria for enhanced response to the chosen organic molecules. The embodiments were chosen and described in order to best explain the principles of the invention and its practical application to thereby enable others skilled in the art to best utilize the invention in various embodiments and with various modifications as are suited to the particular use contemplated. It is intended that the scope of the invention be defined by the claims appended hereto. 

1. A method for detecting 2-chlorophenol or 2,4-dichlorophenol in a test sample, wherein said method comprises the steps of: (1) culturing a Pseudomonas or Escherichia coli cell comprising (a) a reporter gene under the control of the Po promoter inducible by the DmpR protein of Pseudomonas sp. strain CF600, and (b) a Pseudomonas sp. strain CF600 DmpR gene mutated at the coding region of the sensor domain, wherein the coding region of the sensor domain of the mutated Pseudomonas sp. strain 0F600 DmpR gene comprises SEQ ID NO: 3, and wherein said mutation results in enhanced transcriptional activation response to 2-chlorophenol and 2,4-dichlorophenol relative to the response obtained with wild type Pseudomonas sp. strain CF600 DmpR protein; and, (2) detecting the expression of the reporter gene, wherein expression of the reporter gene is indicative of the presence of 2-chlorophenol or 2,4-dichlorophenol. 